JPH10137753A - Method for separating and removing selenium - Google Patents

Method for separating and removing selenium

Info

Publication number
JPH10137753A
JPH10137753A JP8302721A JP30272196A JPH10137753A JP H10137753 A JPH10137753 A JP H10137753A JP 8302721 A JP8302721 A JP 8302721A JP 30272196 A JP30272196 A JP 30272196A JP H10137753 A JPH10137753 A JP H10137753A
Authority
JP
Japan
Prior art keywords
selenium
resin
reducing substance
solution
ion exchange
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP8302721A
Other languages
Japanese (ja)
Inventor
Katsuhiko Yano
勝彦 矢野
Jiyunya Watanabe
純哉 渡辺
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Mitsubishi Chemical Corp
Original Assignee
Mitsubishi Chemical Corp
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Mitsubishi Chemical Corp filed Critical Mitsubishi Chemical Corp
Priority to JP8302721A priority Critical patent/JPH10137753A/en
Publication of JPH10137753A publication Critical patent/JPH10137753A/en
Pending legal-status Critical Current

Links

Landscapes

  • Treatment Of Water By Ion Exchange (AREA)

Abstract

PROBLEM TO BE SOLVED: To simply remove selenium in waste water by allowing a solution contg. selenium compounds and/or their salts to contact with an ion exchange resin or chelate resin, on each of which a reducing substance is supported, to adsorb selenium on the resin. SOLUTION: In this method, a solution contg. selenic acid, selenous acid and/or their salts is allowed to contact with an ion exchange resin or chelate resin, on each of which a reducing substance is supported. As the reducing substance, any reducing substance can be used provided that it can be supported on an ion exchange resin or chelate resin without adversely affecting its reducing power. For example, hydrazine, hydroxylamine, copper(I) ions, or the like can be used as the reducing substance. An adequate amount of such a reducing substance is dissolved into water to allow an aq. solution thus obtained to contact with the ion exchange resin or chelate resin and to support the reducing substance on the resin and then, the solution contg. selenium compounds and/or their salts is allowed to contact with the resulting ion exchange resin or chelate resin at >=70 deg.C to reduce the selenium compounds and/or their salts to metal selenium. Thus, the ion exchange resin or chelate resin, each supporting the reducing substance, has high selenium-removal efficiency and also, can repeatedly be used by repeatedly allowing the resin to contact with the aq. solution of the reducing substance.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、簡便で安価な水中
のセレン化合物の分離又は除去方法に関するものであ
り、化学工業、冶金工業、電気・電子作業等の環境保全
分野に属する用水、排水処理に係わるものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a simple and inexpensive method for separating or removing selenium compounds in water, and for treating water and wastewater belonging to the environmental protection fields such as chemical industry, metallurgy industry and electric / electronic work. It is related to.

【0002】[0002]

【従来の技術】セレンは有害であるため、その排水基準
及び環境基準は、各0.1ppm及び0.01ppmと
厳しく定められている。これらの基準を達成するため
に、産業界では、省資源、省エネルギー的でかつ効率的
なセレン分離システムの出現が待望されている。水中の
セレン化合物は、主に4価のセレンである亜セレン酸と
6価のセレンであるセレン酸の形で存在している。一般
にセレンを含む液の排水処理では、多量の共存塩の存在
下、微量のセレン化合物を除去することが求められる
が、そのような状況でのセレン除去は困難を伴う。
2. Description of the Related Art Since selenium is harmful, its effluent standards and environmental standards are strictly set at 0.1 ppm and 0.01 ppm, respectively. In order to achieve these standards, there is a long-awaited need in the industry for a resource-saving, energy-saving and efficient selenium separation system. Selenium compounds in water exist mainly in the form of selenous acid, which is tetravalent selenium, and selenic acid, which is hexavalent selenium. Generally, in wastewater treatment of a liquid containing selenium, it is required to remove a small amount of a selenium compound in the presence of a large amount of coexisting salt, but selenium removal in such a situation involves difficulties.

【0003】そのセレンを除去することの困難性は、セ
レンの化学構造に由来する。一般に微量の重金属イオン
の除去には種々のキレート樹脂が用いられる。しかし、
キレート樹脂は、鉄、銅などのカチオン性の重金属イオ
ンを選択的に除去するために用いられ、セレンのような
酸素が結合したアニオンとして存在する金属を除去する
には適さない。これは、セレン酸、亜セレン酸が酸素が
結合した構造をもつため、セレン原子が他の配位子と直
接相互作用しにくくなっているためである。
[0003] The difficulty in removing selenium comes from the chemical structure of selenium. Generally, various chelating resins are used for removing a trace amount of heavy metal ions. But,
Chelate resins are used to selectively remove cationic heavy metal ions such as iron and copper, and are not suitable for removing metals such as selenium that exist as oxygen-bound anions. This is because selenic acid and selenous acid have a structure in which oxygen is bonded, and thus it is difficult for the selenium atom to directly interact with other ligands.

【0004】従来、排水中セレンの除去方法としては、
いくつかの方法が知られている。例えば、セレンを吸着
する樹脂として、エポラスK―6(ミヨシ油脂製)等の
アニオン交換樹脂が知られているが、これらはセレンを
アニオン交換により捕捉、吸着するため、セレン濃度が
希薄で高濃度の共存塩が存在する産業排水からのセレン
除去には効果を発揮しない。また、アニオン交換樹脂に
ビスムチオールIIやアゾチオフィリンジスルホン酸など
を担持した樹脂が4価セレン(亜セレン酸)を吸着する
ことが報告されているが、これらの薬品は高価なため排
水処理への工業的利用には不適当である。また、特開平
8−132074号及び同8−224585号各公報に
記載のように、化学的還元又は電気的還元によりセレン
をメタル化して除去する方法は、還元したメタルを回収
する工程が必要なため、プロセス的に煩雑になる。
Conventionally, methods for removing selenium from wastewater include:
Several methods are known. For example, as a resin for adsorbing selenium, an anion exchange resin such as Eporus K-6 (made by Miyoshi Oil & Fats) is known. Has no effect on the removal of selenium from industrial effluent in which coexisting salts are present. In addition, it has been reported that resins carrying bismuthiol II or azothiophyllin disulfonic acid on anion exchange resins adsorb tetravalent selenium (selenous acid). Not suitable for industrial use. In addition, as described in JP-A-8-132044 and JP-A-8-224585, the method of metallizing and removing selenium by chemical reduction or electrical reduction requires a step of recovering the reduced metal. Therefore, the process becomes complicated.

【0005】[0005]

【発明が解決しようとする課題】本発明は、上記実情に
鑑みて為されたものであり、その目的は、排水中のセレ
ンを、高濃度の共存塩の存在下、簡便で、安価に除去す
る方法を提供することである。
SUMMARY OF THE INVENTION The present invention has been made in view of the above circumstances, and has as its object to easily and inexpensively remove selenium from wastewater in the presence of a high concentration of coexisting salts. Is to provide a way to

【0006】[0006]

【課題を解決するための手段】本発明は、特定の条件で
セレン化合物又はその塩類を含有する溶液を処理するこ
とにより上記目的が達成されることを見出して完成され
たものである。すなわち本発明は、「セレン化合物又は
その塩類を含有する溶液を、還元性物質を担持したイオ
ン交換樹脂又はキレート樹脂に接触させて、セレンを吸
着させることを特徴とするセレンの分離又は除去方
法」、である。
Means for Solving the Problems The present invention has been accomplished by finding that the above object can be achieved by treating a solution containing a selenium compound or a salt thereof under specific conditions. That is, the present invention provides a method for separating or removing selenium, which comprises contacting a solution containing a selenium compound or a salt thereof with an ion-exchange resin or a chelate resin carrying a reducing substance to adsorb selenium. ,.

【0007】セレン化合物又はその塩類を含む液を、還
元性物質と直接接触させた場合セレンは還元できるが、
還元されたセレンを濾過等により除去することが必要に
なる。還元されたセレンは微細な粒子として存在するた
め、濾過による除去は困難である。ここで、還元性物質
を担持したイオン交換樹脂又はキレート樹脂を用いれ
ば、還元されたセレン化合物が樹脂に近接するため、セ
レンが樹脂内に析出、吸着される。よって、還元された
セレンを濾過等により除去する必要がない。また、還元
性物質をイオン交換樹脂又はキレート樹脂上に担持すれ
ば、還元性物質がイオン交換樹脂又はキレート樹脂上に
濃縮され、還元性物質濃度が高くなり反応が進み易くな
る。
When a liquid containing a selenium compound or a salt thereof is brought into direct contact with a reducing substance, selenium can be reduced.
It is necessary to remove the reduced selenium by filtration or the like. Since reduced selenium exists as fine particles, removal by filtration is difficult. Here, if an ion-exchange resin or a chelate resin carrying a reducing substance is used, the reduced selenium compound comes close to the resin, so that selenium is precipitated and adsorbed in the resin. Therefore, there is no need to remove the reduced selenium by filtration or the like. Further, when the reducing substance is supported on the ion exchange resin or the chelate resin, the reducing substance is concentrated on the ion exchange resin or the chelate resin, and the concentration of the reducing substance increases, so that the reaction proceeds easily.

【0008】また、還元性物質を担持させたイオン交換
樹脂又はキレート樹脂に用いずに、系内に還元性物質と
イオン交換樹脂又はキレート樹脂を単に混在させただけ
の状態で、セレン化合物又はその塩類を含む溶液をこれ
らと接触させた場合は、還元されたセレンが樹脂内に十
分拡散しないためセレンが樹脂内に十分吸着されず、一
部が樹脂外に存在する。このため、セレンの除去工程が
煩雑になる。
Further, a selenium compound or a selenium compound thereof is used in a state where a reducing substance and an ion exchange resin or a chelate resin are simply mixed in a system without using the ion exchange resin or the chelate resin carrying the reducing substance. When a solution containing salts is brought into contact with them, the reduced selenium does not sufficiently diffuse into the resin, so that selenium is not sufficiently adsorbed in the resin and a part of the selenium exists outside the resin. For this reason, the selenium removal step becomes complicated.

【0009】[0009]

【発明の実施の形態】以下、本発明につき詳細に説明す
る。本発明において、セレン化合物又はその塩類を含有
する溶液としては、セレン酸、亜セレン酸又はそれらの
塩類の溶液が挙げられる。このとき、該溶液としてはセ
レン化合物又はその塩類と高濃度の他の塩類(アルカリ
金属イオン、アルカリ土類金属イオン、塩素イオン、硫
酸イオン等)を含有し、セレン化合物又はその塩類の濃
度が希薄である水溶液であってもよい。本発明の分離又
は除去方法によれば、上記のいずれの溶液の場合でも処
理後の溶液にはセレンが極微量しか残存しない程度にセ
レンを分離・除去できる。
DESCRIPTION OF THE PREFERRED EMBODIMENTS The present invention will be described below in detail. In the present invention, examples of the solution containing a selenium compound or a salt thereof include a solution of selenic acid, selenous acid or a salt thereof. At this time, the solution contains a selenium compound or a salt thereof and a high concentration of another salt (alkali metal ion, alkaline earth metal ion, chloride ion, sulfate ion, etc.), and the concentration of the selenium compound or a salt thereof is low. May be used. According to the separation or removal method of the present invention, selenium can be separated and removed to the extent that only a trace amount of selenium remains in the treated solution in any of the above solutions.

【0010】本発明において、イオン交換樹脂又はキレ
ート樹脂としては、「機能性高分子シリーズ キレート
樹脂・イオン交換樹脂 講談社サイエンティフィク社
(1986年8月1日発行)」や「ダイヤイオンマニュ
アル 三菱化学社」等に記載されている様な、既に公知
のものが特に制限なく用いられ、ゲル型のものでも多孔
性のものでも使用できる。
In the present invention, examples of the ion exchange resin or chelate resin include “functional polymer series chelate resin / ion exchange resin Kodansha Scientific Inc. (issued on August 1, 1986)” and “Diaion Manual Mitsubishi Chemical Corporation”. Known ones, such as those described in "Corporation", can be used without any particular limitation, and either a gel type or a porous type can be used.

【0011】また、還元性物質としては、上記イオン交
換樹脂又はキレート樹脂に担持でき、還元性が損なわれ
ないものであれば、どんな還元性物質でも使用できる。
具体的にはヒドラジン、ヒドロキシルアミン、銅(I)
イオン、鉄(II)イオン、スズ(II)イオン、水素化ホ
ウ素化合物、亜硫酸イオン、次亜硫酸イオン、次亜リン
酸イオン等が挙げられる。好ましくはヒドラジン又はヒ
ドロキシルアミンが用いられる。特に好ましくはヒドラ
ジンが用いられる。また、還元性物質は1種類を単独で
用いても、複数の還元性物質を共存させてもよい。
As the reducing substance, any reducing substance can be used as long as it can be supported on the above-mentioned ion exchange resin or chelating resin and the reducing property is not impaired.
Specifically, hydrazine, hydroxylamine, copper (I)
Ion, iron (II) ion, tin (II) ion, borohydride compound, sulfite ion, hyposulfite ion, hypophosphite ion and the like. Preferably, hydrazine or hydroxylamine is used. Particularly preferably, hydrazine is used. Further, one kind of the reducing substance may be used alone, or a plurality of reducing substances may coexist.

【0012】還元性物質のイオン交換樹脂又はキレート
樹脂への担持は、イオン交換樹脂又はキレート樹脂と、
還元性物質を適量溶解させた水溶液を接触させればよ
い。たとえば、還元性物質としてヒドラジン又はヒドロ
キシルアミンを用い、また担体としてカチオン交換樹脂
を用いる場合は、H形に調整したカチオン交換樹脂に、
ヒドラジン又はヒドロキシルアミン溶液を接触させれば
よい。
The loading of the reducing substance on the ion-exchange resin or the chelate resin is performed by combining the ion-exchange resin or the chelate resin with:
An aqueous solution in which an appropriate amount of a reducing substance is dissolved may be brought into contact. For example, when hydrazine or hydroxylamine is used as the reducing substance and a cation exchange resin is used as the carrier, the cation exchange resin adjusted to the H form is
A hydrazine or hydroxylamine solution may be brought into contact.

【0013】上記の還元性物質を担持したイオン交換担
体又はキレート樹脂をセレン化合物又はその塩類を含有
する溶液に接触させればセレン化合物又はその塩類は、
担持した還元性物質の作用により0価の金属セレンにま
で還元される。還元性物質は樹脂に担持されており、還
元されたセレンが樹脂に近接しているため、セレンは樹
脂内に析出、吸着される。この様にして、セレン化合物
又はその塩類を含有する溶液を還元性物質を担持したイ
オン交換樹脂又はキレート樹脂に通液するだけで溶液中
のセレン化合物を分離、除去できる。セレン化合物とし
ては、4価セレンが特に除去される。ここで、温度は、
70℃以上であることが好ましく、それ以下の温度では
反応が遅く、効率が劣る傾向にある。この温度は高いほ
ど除去効率が高くなり、実用上80℃から95℃が最も
好ましい。また、セレンの還元反応に消費された還元性
物質は、その時点で活性を失うが、還元性物質溶液を適
宜、母体樹脂に接触させ担持させることができる。この
ため、何度でも繰り返し使用できる。
The selenium compound or its salt can be obtained by contacting the ion-exchange carrier or chelating resin carrying the above-mentioned reducing substance with a solution containing the selenium compound or its salt.
It is reduced to zero-valent metal selenium by the action of the loaded reducing substance. Since the reducing substance is supported by the resin and the reduced selenium is close to the resin, the selenium is precipitated and adsorbed in the resin. In this manner, the selenium compound in the solution can be separated and removed only by passing the solution containing the selenium compound or salts thereof through an ion exchange resin or a chelate resin supporting a reducing substance. As the selenium compound, tetravalent selenium is particularly removed. Where the temperature is
The temperature is preferably 70 ° C. or higher, and at a temperature lower than 70 ° C., the reaction tends to be slow and efficiency tends to be poor. The higher this temperature is, the higher the removal efficiency is, and practically the most preferable temperature is 80 to 95 ° C. Further, the reducing substance consumed in the reduction reaction of selenium loses its activity at that point, but the reducing substance solution can be appropriately brought into contact with the base resin to be supported. Therefore, it can be used any number of times.

【0014】イオン交換樹脂又はキレート樹脂に担持す
る還元性物質は、従来セレンの捕捉剤として知られてい
るビスムチオールIIやアゾチオフィリンジスルホン酸に
比べ、安価であり廃水処理への利用に適当である。ま
た、本発明においては共存塩の存在下においても、還元
反応は進行し、セレンは吸着除去できる。
The reducing substance carried on the ion-exchange resin or the chelate resin is less expensive than bismuthiol II and azothiophyllin disulfonic acid, which are conventionally known as selenium scavengers, and is suitable for use in wastewater treatment. . In the present invention, the reduction reaction proceeds even in the presence of a coexisting salt, and selenium can be adsorbed and removed.

【0015】本発明の分離又は除去方法は、従来公知の
イオン交換樹脂又はキレート樹脂による溶液中のイオン
の吸着分離法と同様に、バッチ法又はカラム法により行
うことができる。上記の方法と同様にして、本発明の分
離又は除去方法は、化学工業、冶金工業、電気、電子産
業等におけるセレンを含有する産業排水の処理に有効に
利用することができる。
The separation or removal method of the present invention can be carried out by a batch method or a column method in the same manner as the conventionally known method of separating and adsorbing ions in a solution using an ion exchange resin or a chelate resin. Similarly to the above method, the separation or removal method of the present invention can be effectively used for the treatment of industrial wastewater containing selenium in the chemical industry, metallurgy industry, electricity, electronics industry and the like.

【0016】[0016]

【実施例】【Example】

[実施例1]H形にコンディショニングしたダイヤイオ
ンSK102の10ml(方法は「ダイヤイオンマニュ
アル」(三菱化学)参照)にヒドラジン水和物0.15
gを含むヒドラジン水溶液100mlを加え、三角フラ
スコ中、25℃で2時間振盪した。吸着前後のヒドラジ
ン量を酸滴定した結果、ヒドラジンの担持量は、0.3
0mモルであった。この樹脂を濾過し、10倍量の水で
洗浄した後、さらに樹脂を濾過し、ヒドラジン担持樹脂
を得た。この樹脂をジムロートコンデンサーをつけた2
00ml四つ口フラスコに入れ、さらに亜セレン酸10
ppm溶液100mlを加え、攪拌下反応温度80℃で
2時間保持した。液を冷却後、溶液中のセレン量をIC
P発光分析装置にて分析した。
[Example 1] Hydrazine hydrate 0.15 was added to 10 ml of Diaion SK102 conditioned to H-form (for the method, see "Diaion Manual" (Mitsubishi Chemical)).
g of hydrazine aqueous solution containing 100 g was added and shaken at 25 ° C. for 2 hours in an Erlenmeyer flask. As a result of acid titration of the amount of hydrazine before and after adsorption, the amount of hydrazine carried was 0.3
It was 0 mmol. After filtering this resin and washing with 10 times the amount of water, the resin was further filtered to obtain a hydrazine-supported resin. This resin was fitted with a Dimroth condenser 2
In a 00 ml four-necked flask, add selenous acid 10
100 ml of a ppm solution was added, and the mixture was kept at a reaction temperature of 80 ° C. for 2 hours with stirring. After cooling the liquid, the amount of selenium in the solution is determined by IC
The analysis was performed using a P emission analyzer.

【0017】[比較例1]実施例1におけるヒドラジン
担持樹脂のかわりに、H形ダイヤイオンSK102を用
いた以外は、実施例1と同様の方法を行った。
Comparative Example 1 A method similar to that of Example 1 was performed except that H-type Diaion SK102 was used instead of the hydrazine-supported resin in Example 1.

【0018】[比較例2]実施例1におけるヒドラジン
担持樹脂のかわりに、H形ダイヤイオンSK102を用
い、反応温度を25℃とした以外は、実施例1と同様の
方法を行った。上記実施例1及び比較例1及び同2の結
果を合わせて表1に示す。ヒドラジンを担持した樹脂で
は溶液中のセレン濃度が減少しており、亜セレン酸が還
元され樹脂に吸着されていると考えられる。
Comparative Example 2 An H-type Diaion SK102 was used in place of the hydrazine-supported resin in Example 1, and the same method as in Example 1 was performed except that the reaction temperature was 25 ° C. Table 1 shows the results of Example 1 and Comparative Examples 1 and 2 together. In the resin supporting hydrazine, the selenium concentration in the solution was decreased, and it is considered that selenite was reduced and adsorbed on the resin.

【0019】[0019]

【表1】 [Table 1]

【0020】[実施例2]実施例1における10ppm
亜セレン酸溶液100mlの代わりに、硫酸ナトリウム
を0.1重量% 含む10ppm亜セレン酸溶液100m
lを加えた以外は、実施例1と同様の方法を行った。
[Example 2] 10 ppm in Example 1
Instead of 100 ml of selenous acid solution, 100 m of 10 ppm selenous acid solution containing 0.1% by weight of sodium sulfate was used.
The same method as in Example 1 was performed except that l was added.

【0021】[実施例3]実施例1における10ppm
亜セレン酸溶液100mlの代わりに、硫酸ナトリウム
を1重量% 含む10ppm亜セレン酸溶液100mlを
加えた以外は、実施例1と同様の方法を行った。上記実
施例2及び同3の結果を表2に示す。
Example 3 10 ppm in Example 1
A method similar to that of Example 1 was performed, except that 100 ml of a 10 ppm selenite solution containing 1% by weight of sodium sulfate was added instead of 100 ml of the selenous acid solution. Table 2 shows the results of Examples 2 and 3 described above.

【0022】[0022]

【表2】 [Table 2]

【0023】[0023]

【発明の効果】本発明により、排水中のセレンを、高濃
度の共存塩の存在下においても、簡便で、安価に吸着し
て分離、除去することができると言った顕著な効果が奏
される。
According to the present invention, there is a remarkable effect that selenium in wastewater can be easily and inexpensively adsorbed, separated and removed even in the presence of a high concentration of coexisting salt. You.

Claims (5)

【特許請求の範囲】[Claims] 【請求項1】 セレン化合物又はその塩類を含有する溶
液を、還元性物質を担持したイオン交換樹脂又はキレー
ト樹脂に接触させて、セレンを吸着させることを特徴と
するセレンの分離又は除去方法。
1. A method for separating or removing selenium, which comprises contacting a solution containing a selenium compound or a salt thereof with an ion-exchange resin or a chelate resin carrying a reducing substance to adsorb selenium.
【請求項2】 接触させる温度が70℃以上である請求
項1に記載の方法。
2. The method according to claim 1, wherein the contacting temperature is 70 ° C. or higher.
【請求項3】 還元性物質が、ヒドラジン又はヒドロキ
シルアミンである請求項1に記載の方法。
3. The method according to claim 1, wherein the reducing substance is hydrazine or hydroxylamine.
【請求項4】 セレン化合物又はその塩類が、亜セレン
酸又はその塩類である請求項1に記載の方法。
4. The method according to claim 1, wherein the selenium compound or a salt thereof is selenous acid or a salt thereof.
【請求項5】 セレン化合物又はその塩類を含有する溶
液が、セレン化合物又はその塩類を含有する産業排水で
ある請求項1に記載の方法。
5. The method according to claim 1, wherein the solution containing a selenium compound or a salt thereof is an industrial wastewater containing a selenium compound or a salt thereof.
JP8302721A 1996-11-14 1996-11-14 Method for separating and removing selenium Pending JPH10137753A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP8302721A JPH10137753A (en) 1996-11-14 1996-11-14 Method for separating and removing selenium

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP8302721A JPH10137753A (en) 1996-11-14 1996-11-14 Method for separating and removing selenium

Publications (1)

Publication Number Publication Date
JPH10137753A true JPH10137753A (en) 1998-05-26

Family

ID=17912375

Family Applications (1)

Application Number Title Priority Date Filing Date
JP8302721A Pending JPH10137753A (en) 1996-11-14 1996-11-14 Method for separating and removing selenium

Country Status (1)

Country Link
JP (1) JPH10137753A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2011189300A (en) * 2010-03-16 2011-09-29 Taiheiyo Cement Corp Method for removing selenium
JP2018192417A (en) * 2017-05-17 2018-12-06 株式会社Kri Metal oxoanion complex adsorbent and adsorption method

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2011189300A (en) * 2010-03-16 2011-09-29 Taiheiyo Cement Corp Method for removing selenium
JP2018192417A (en) * 2017-05-17 2018-12-06 株式会社Kri Metal oxoanion complex adsorbent and adsorption method

Similar Documents

Publication Publication Date Title
CA1240521A (en) Recovery of cyanide from waste waters by an ion exchange process
CN103304052A (en) Treatment method of gold extraction cyaniding wastewater containing copper and iron ions with high concentration
JP5603394B2 (en) Method for treating waste liquid containing cesium
EP0355418B1 (en) Process for the treatment of effluents containing cyanide and toxid metals, using hydrogen peroxide and trimercaptotriazine
US4548718A (en) Treating cyanide-containing effluents
US5601722A (en) Method for the preparation of an ion exchanger for cesium ions and method for the regeneration thereof
JPH08224585A (en) Removal of selenium from spent liquor
JPH10137753A (en) Method for separating and removing selenium
JPH02139092A (en) Method of detoxicating waste water containing element mercury
WO1981000728A1 (en) Purification process for spent pickling baths
Germain et al. Plating and cyanide wastes
JPH11235595A (en) Treatment of boron-containing waste water
JP2923757B2 (en) Reduction method of hexavalent selenium
CN108654554B (en) Preparation method of succinic acid surface modified mesoporous alumina adsorbent
SU1309914A3 (en) Method of extracting non-ferrous and/or noble metals from aqueous solutions
RU2608968C1 (en) Method of processing liquid radioactive wastes
JP3586165B2 (en) Treatment of wastewater containing selenium
JPH09308891A (en) Removal of selenium oxide in water
SU1490098A1 (en) Method of purifying waste water from copper and nickel ions
JP4269442B2 (en) Method for separating and recovering palladium
JPH1157464A (en) Method for removing selenium
JP2000144472A (en) Refining treatment of salt water for electrolysis
JPH06146098A (en) Method for recovering and reproducing sn plating liquid
JP2706276B2 (en) How to remove silver
JP2608825B2 (en) Purification method of aqueous hydrogen peroxide solution

Legal Events

Date Code Title Description
A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20040721

A131 Notification of reasons for refusal

Free format text: JAPANESE INTERMEDIATE CODE: A131

Effective date: 20051206

A02 Decision of refusal

Free format text: JAPANESE INTERMEDIATE CODE: A02

Effective date: 20060411